CA2037814A1

CA2037814A1 - Catalyst and method for catalytically decomposing nitrogen oxides

Info

Publication number: CA2037814A1
Application number: CA002037814A
Authority: CA
Inventors: Shuichi Kagawa; Yasutake Teraoka
Original assignee: Tosoh Corp
Current assignee: Tosoh Corp
Priority date: 1990-03-09
Filing date: 1991-03-08
Publication date: 1991-09-10
Also published as: AU7269991A; AU649586B2; US5219545A

Abstract

TYS-8435-US,CA
CATALYST AND METHOD FOR CATALYTICALLY
DECOMPOSING NITROGEN OXIDES
ABSTRACT OF THE DISCLOSURE
A catalyst and a method for catalytically decom-posing nitrogen oxides, wherein the catalyst comprises a zeolite having a mole ratio of SiO2/Al2O3 of at least 20, and containing (i) copper ions and (ii) (a) transition metal ions other than copper ions, (b) at least one alkaline earth metal ion selected from calcium, strontium and barium ions, (c) yttrium ions, or (a) silver ions.

Description

TYS-8435-US,CA

1- 2~37814 CATALYST AND METHOD FOR CATALYTICALLY
DECOMPOSING NITROGEN OXIDES

BACKGROUND OF THE INVENTION
l. Field of the Invention The present invention relates to a catalyst for removing nitrogen oxides from a gas containing the same, and a method of using the catalyst. More specifi-cally, it relates to a catalyst for catalytically decomposing nitrogen oxides, and a method of using the same. The catalyst of the present invention suffers little deterioration even in the presence of oxygen or a sulfur oxide.

2. Description of the Related Art Nitrogen oxides in combustion waste gases discharged from, for example, industrial plants and automobiles, are the cause of photochemical smog, and the development of methods of eliminating these substances is a crucial and urgent social need from the standpoint of environmental protection. Among the nitrogen oxides, nitric monoxide (NO) is particularly difficult to remove, and various methods of removing this substance have been investiqated. For example, the catalytic reduction method is considered effective, and rapid progress has been made in the development of this method. This method, however, requires the use of a reducing agent such as ammonia, hydrogen or carbon monoxide, and further, requires special equipment for the recovery or decomposition of any unreacted reducing agent. In contrast, the catalytic decomposition method does not require a special additive, such as a reducing agent, and can decompose and separate a nitrogen oxide into nitrogen and oxygen merely by passing the nitrogen oxide through a catalyst bed. Further, the process is advantageously simple, and therefore, has been regarded as the most preferable method. According to previous ~ - 2 - 2037814 research, a NO decomposition activity was observed in Pt, CuO, and Co3O4 , among others, but because all of these substances are poisoned by oxygen, which is the decomposition product, they are not practically useful as catalysts.
Accordingly, the present inventors carried out intensive studies of catalysts useful for catalytic decomposition, and found that several kinds of zeolites with exchanged copper ions exhibit a stable decomposi-tion activity. Further, the inventors found that azeolite containing copper ions and having a specific crystal structure not only exhibits an extremely stable and high activity as a catalytic decomposition catalyst for NO, but also maintains that activity at the same level even in the presence of a sulfur oxide (see Japanese Unexamined Patent Publication (Kokai) NO.
60-125250).
The above-mentioned catalyst, however, does not have a satisfactory activity or heat resistance at high temperatures, and thus can not be put to practical use.
The present inventors have made extensive and intensive studies of the above-mentioned problems, and thus completed the present invention.
SUMMARY OF THE INVENTION
Accordingly, an object of the present invention is to provide a catalytic decomposition catalyst which can efficiently remove nitrogen oxides in the combustion waste gas discharged from, for example, industrial plants and automobiles, even at high temperatures and without the use of ammonia as a reducing agent, and further, maintain a high level of activity even in the presence of a sulfur oxide and oxygen.
Other objects and advantages of the present invention will be apparent from the following description.
In accordance with the present invention, there is ` ~ 3 ~ 2~378~4 provided a catalyst for catalytically decomposing nitrogen oxides comprising a zeolite having a mole ratio of SiO2/A12O3 of at least 20, and containing (i), copper ions and (ii)(a) transition metal ions other than copper ions, (b) at least one alkaline earth metal ion selected from calcium, strontium and ~arium ions, (c) yttrium ions, or (d) silver ions.
In accordance with the present invention, there is also provided a method of catalytically decomposing nitrogen oxides from a gas containing the same, which comprises bringing said catalyst into contact with the gas containing nitrogen oxides.
DESCRIPTION OF THE PREFERRED EMBODIMENTS
The present invention will now be described in more detail.
Preferably, the zeolite usable in the present invention has a mole ratio of SiO2/A12O3 of at least 20.
The upper limit of the mole ratio of SiO2/A12O3 is not particularly limited, but when the mole ratio of SiO2/A12O3 is less than 20, a satisfactory heat resistance can not be obtained. In general, a zeolite having a mole ratio of SiO2/A12O3 of about 20 to 200 is used.
Typical examples of the zeolite constituting the catalyst of the present invention are zeolites such as ZSM-5, ZSM-8 ZSM-ll, ZSM-12, ZSM-20, and ZSM-35.
Preferably, ZS~-5 is used. The methods of preparation of these zeolites are not particularly limited, and zeolites such as Mordenite, Ferrierite, Y-type zeolite, and L-type zeolite subjected to dealumination also may be used. These zeolites can be used either as such or after treatment with an ammonium salt or a mineral acid and NH4 ion exchange or H ion exchange, before use.
The incorporation of (i) copper ions and (ii)(a) transition metal ions other than copper ions, (b) at least one al~aline earth metal ion selected from calcium, strontium and barium ions, (c) yttrium ions, - 4 - 2~37814 (d) silver ions in a zeolite having a mole ratio of SiO2/A12O3 of at least 20 is essential to the catalytic decomposition catalyst of the present invention.
There is no particular limitation on the method of incorporating copper ions and transition metal ions other than copper ions, at least one alkaline earth metal ion selected from calcium, strontium and barium ions, yttrium ions, or silver ions in the above-described zeolite, but an ion exchange method is preferred. The ion exchange method may be a method generally practiced in the art. For example, the ion exchange may be conducted by using an aqueous solution containing copper ions and transition metal ions other than copper ions, calcium, strontium or barium ions, yttrium ions, or silver ions. Alternatively, the ion exchange may be conducted by an ion exchange with copper ions followed by an ion exchange with other metal ions, or an ion exchange with metal ions other than copper ions followed by an ion exchange with copper ions. The concentrations of copper ions and other metal ions in the aqueous solution during the ion exchange can be appropriately set in accordance with the degree of ion exchange.
The copper ions and other metal ions can be used in the form of soluble salts such as, for example, nitrates, acetates, oxalates, and chlorides.
During the ion exchange of copper ions as described above, ammonia also may be added to control the pH to thereby increase the copper ion content in the zeolite.
Since the copper ion existing at the ion exchange site of the zeolite is the active site, the copper is preferably exchznged at the ion exchange site. Also, the metal ions other than copper ions are preferably ion-exchanged at the ion exchange site, but the effect thereof also can be exhibited when these metal ions are supported on the zeolite as a compound such as oxide.
There is no particular limitation on the transition _ 5 _ 203781~

metal ions used in the present invention, and preferred examples thereof include cobalt, nickel, chromium, iron, manganese, zinc and platinum ions.
The sample subjected to the ion exchange treatment is subjected to solid-liquid separation, washing and drying before use, and further, can be calcined if necessary.
The degree of ion-exchange of copper is preferably 0.01 to l.S, more preferably O.l to 0.8, as represented in terms of the Cu/Al atomic ratio, and the degree of ion-exchange of metals other than copper is preferably 0.01 or more, more preferably 0.05 to 1, in terms of the atomic ratio to aluminum. When the CuJAl atomic ratio is less than 0.01, the number of copper ions, which are active sites, is not sufficient to provide the required catalytic activity, and when the ratio exceeds 1.5, copper will exist on the zeolite surface as a compound such as oxide, and thus the effect corresponding to the increased content of the copper ions may not be obtained. When the degree of ion-exchange of metals Gther than copper is less than 0.01, in terms of the atomic ratio to aluminum, the effect provided by the coexistence of the metal ions other than copper is small, and thus a satisfactory heat resistance may not be obtained.
The SiO2/Al203 mole ratio of the catalytic decomposition catalyst of the present invention is substantially the same as the SiO2/Al203 mole ratio of the zeolite base material used. Also, the crystal structure of the catalytic decomposition catalyst after ion exchange remains substantially unchanged, compared with that before the ion exchange.
Further, the catalytic decomposition catalyst of the present invention can be used as a mixture molded with a binder, such as a clay mineral, and further, the zeolite may be previously molded and copper and other metal ions incorporated by ion exchange into the molded product. The binder usable during the molding of the zeolite may include clay minerals such as kaolin, attapulgiie, montmorillonite, bentonite, allophane, and sepiolite. Alternatively, a binderless zeolite molded product obtained by a direct molding without the use of a binder may be used. Further, it is also possible to coat a base material in a honeycomb form made of cordierite or a metal, with a zeolite.
A catalytic decomposition of nitrogen oxides in the waste gas can be performed by bringing the catalytic decomposition catalyst of the present invention into contact with a waste gas containing nitrogen oxides.
The catalytical decomposition of nitrogen oxides in a waste gas is preferably carried out under the conditions of a temperature of 100C to 1000C, more preferably 150C to 800C and a contact time with the catalyst of 0.01 to 10 g-sec/ml, more preferably 0.03 to 8 g.sec/ml.
The above-mentioned catalytic decomposition catalyst can exhibit a catalytic performance equal to that of the conventional zeolite catalyst having copper supported thereon, even when applied to a waste gas containing, for example, ammonia, carbon monoxide, hydrocarbons, water, oxygen, and sulfur oxides.
2S As disclosed in Japanese Unexamined Patent Publica-tion (Kokai~ No. 60-125250, a crystalline alumino-silicate having a specific structure containing copper ions can efficiently remove nitrogen oxides even from a waste gas not containing a reducing agent. This is because a specific structure of the crystalline aluminosilicate facilitates the redox cycle of copper ions subjected to an ion exchange, and the nitrogen oxides are decomposed through the redox cycle into nitrogen and oxygen. Further, the copper ions are less susceptible to poisoning by oxygen as a decomposition product of the nitrogen oxides, which enables the decomposition activity to be maintained at a high level 2037~1~
for long periods.
In the above-mentioned crystalline aluminosilicate ion-exchanged with copper ions, however, the reduction of the copper ions is excessive at a high temperature, which hinders the redox cycle of the copper ions, and thus a satisfactory activity cannot be obtained.
The catalyst of the present invention comprises a zeolite, and incorporated therein, (i) copper ions and (ii)(a) transition metal ions other than copper ions, (b) at least one alkaline earth metal ion selected from calcium, strontium and ~arium ions, (c) yttrium ions, or ~d) silver ions. The coexistence of the specific metal ions other than copper ions cbntributes to not only an improvement in the heat resistance of the zeolite per se but also the prevention of an excessive reduction of the copper ions. This accelerates the redox cycle of the copper ions, and thus a catalytic decomposition catalyst havinq a high activity and stability, even at high temperatures, is obtained.
The nitrogen oxide catalytic decomposition catalyst of the present invention can efficiently remove nitrogen oxides in a combustion waste gas even at a high temperature, without the use of a reducing agent such as ammonia, and further, has a very high heat resistance.
Therefore, nitrogen oxides can be removed from a waste gas even at a high temperature by bringing the catalyst of the present invention into contact with the waste gas.
ExamPles The present invention will now be described in more detail by, but is by no means limited to, the following Examples.
ExamPle 1 An a~ueous sodium silicate solution (SiO2:
153 g/liter; Na20: 50 g/liter; A1203: 0.8 g/liter) and an aqueous aluminum sulfate solution (A1203:
38.4 g/liter; K2S04: 275 g/liter) were continuously ~ed respectively at rates of 3.2 liters/hr and 0.8 literJhr into an overflow type reactor having a net volume of 2 liters, while stirring. The reaction temperature was 30 to 32C, and the pH of the discharged slurry was 6.4 to 6.6.
The discharged slurry was subjected to solid-liquid separation, and the solid was thoroughly washed with water to obtain a granular amorphous aluminosilicate uniform compound having an Na2O content of 1.72~ by weight, an A12O3 content of 2.58% by weight, an SiO2 content of 39.3~ by weight, and an H2O content of 56.4%
by weight. An autoclave was charged with 2,840 g of the uniform compound and 5160 g of a 1.39~ by weight aqueous NaOH solution, and crystallization was effected at 160C
for 72 hr with stirring. The product was subjected to solid-liquid separation, and the solid was washed with water and dried to obtain a ZSM-5 type zeolite. The zeolite was subjected to a chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
1.1 Na2O, A12O3 and 23.3 SiO2 To one liter of a 0.012 N aqueous cobalt nitrate solution was added 10 g of this zeolite, and the mixture was stirred at 60C for one day and then washed to obtain a zeolite ion-exchanged with cobalt. Subse-quently, the zeolite thus obtained was added to one liter of a 0.024 N aqueous copper acetate solution. The mixture was stirred at 60C for one day, washed, and dried to prepare a catalyst 1. The catalyst 1 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.43 CoO, 0.75 CuO, A12O3 and 23.3 SiO2.
Example 2 A catalyst 2 was prepared in the same manner as that of Example 1, except that 10 g of the ZSM-5 type zeolite prepared in Example 1 was used and nickel 9 2~37~

acetate was used instead of cobalt nitrate.
The catalyst 2 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.60 ~liO, 0.75 CuO, A12O3 and 23.3 SiO2.
Example 3 A catalyst 3 was prepared in the same manner as that of Example 1, except that 10 g of the ZSM-5 type zeolite prepared in Example 1 was used and chromium acetate was used instead of cobalt nitrate.
The catalyst 3 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an ar.hydrous basis:
0.09 Cr2O3 , 1.05 CuO, A12O3 and 23.3 SiO2.
Example 4 A catalyst 4 was prepared in the same manner as that of Example 1, except that 10 g of the ZSM-5 type zeolite prepared in Example 1 was used and iron nitrate was used instead of cobalt nitrate.
The catalyst 4 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.41 FeO, 0.92 CuO, A12O3 and 23.3 SiO2.
2xam~1e 5 The catalyst prepared in Examples 1, 2, 3 and 4 were used for evaluation of the catalytic decomposition performance. The catalysts were press-molded and then pulverized to regulate the granule size to 42 to 80 mesh, and 2 cc of the granules was filled in an atmospheric pressure fixed bed flow type reaction tube.
A pretreatment was conducted in a helium gas at 500~C
for one hr, and a helium gas containing 0.48% of NO was passed through the reaction tube in such a manner that the contact time was 4.0 g.sec/ml.

lO- 20378~4 The NO conversions at respective temperatures are shown in Table 1.

Table 1 NO conversion (%) Temp.
Catalyst Catalyst Catalyst Catalyst Comparative ExamPle 1 To one liter of a 0.012 N aqueous copper acetate solution was added 10 g of the ZSM-5 type zeolite prepared in Example 1. The mixture was stirred at 60C
for one day, washed, and dried to prepare a comparative catalyst 1. The comparative catalyst 1 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios on an anhydrous basis:
0.64 Na2O, 0.69 CuO, A12O3 and 23.3 SiO2.
Comparative Example 2 The catalyst prepared in Comparative Example 1 was used for evaluation of the catalytic decomposition performance in the same manner as that of Example 5.
The results are shown in Table 2.

11 ~037~

Table 2 Temp. NO conversion (%) 700C l0 Example 6 A catalyst 5 was prepared in the same manner as that of Example l, except that l0 g of the ZSM-5 type zeolite prepared in Example l was used and manganese nitrate was used instead of cobalt nitrate.
The catalyst 5 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.68 MnO, 0.71 CuO, Al203 and 23.3 SiO2.
Example 7 A catalyst 6 was prepared in the same manner as that of Example 1, except that 10 g of the ZSM-5 type zeolite prepared in Example l was used and zinc acetate was used instead of cobalt nitrate.
The catalyst 6 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.62 ZnO, 0.76 CuO, Al2O3 and 23.3 SiO2.
Example 8 A catalyst 7 was prepared in the same manner as that of Example 1, except that l0 g of the ZSM-5 type zeolite prepared in Example 1 was used and chloro-platinic acid was used instead of cobalt nitrate.
The catalyst 7 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides `` - 12 - 203~14 on an anhydrous basis:
0.15 PtO, 1.07 CuO, A12O3 and 23.3 SiO2.
Exam~le 9 The catalyst prepared in Examples 6, 7 and 8 was used for evaluation of the catalytic decomposition performance in the same manner as that of Example S.
The results are shown in Table 3.

Table 3 NO conversion (~) Temp.
Catalyst 6 7 700C 28 1~ 16 ExamPle 1 0 An aqueous sodium silicate solution (SiO2:
153 g/liter; Na2O: 50 g/liter; A12O3: 0.8 g/liter) and an aqueous aluminum sulfate solution (A12O3:
38.4 g/liter; H2SO4: 275 g/liter) were continuously fed respectively at rates of 3.2 liters/hr and 0.8 liter/hr into an overflow type reactor having a net volume of 2 liters, while stirring. The reaction temperature was 30 to 32C, and the pH of the discharged slurry was 6.4 to 6.6.
The discharged slurry was subjected to solid-liquid separation, and the solid was thoroughly washed with water to obtain a granular amorphous aluminosilicate uniform compound having an Na2O content of 1.72% by weight, an A12O3 content of 2.58% by weight, an SiO2 content of 39.3% by weight, and an H2O content of 56.4%
by weight. An autoclave was charged with 2,840 g of the uniform compound and 5,160 g of a 1.39% by weight - 13 - 203781~

aqueous NaOH solution, and crystallization was effected at 160C for 72 hr with stirring. The product was subjected to solid-liquid separation, and the solid was washed with water and dried to obtain a ZSM-5 type zeolite. The zeolite was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
1.1 ~a2O, A12O3 and 23.3 SiO2.
To one liter of a 0.012 N aqueous calcium nitrate solution was added 10 g of this zeolite. The mixture was stirred at 60C for one day and then washed to obtain a zeolite ion-exchanged with calcium. Subse-quently, the zeolite thus obtained was added to one liter of a 0.024 N aqueous copper acetate solution. The mixture was stirred at 60C for one day, washed and dried to prepare a catalyst 8. The catalyst 8 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.45 CaO, 0.65 CuO, A12O3 and 23.3 SiO2.
Example 11 A catalyst 9 was prepared in the same manner as that o~ Example 10, except that 10 g of the ZSM-5 type zeolite prepared in Example 10 was used and strontium acetate was used instead of calcium nitrate.
The catalyst 9 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.25 SrO, 0.88 CuO, A12O3 and 23.3 SiO2.
Example 12 A catalyst 10 was prepared in the same manner as that or Example 10, except that 10 g of the ZSM-5 type zeolite prepared in Example 10 was used and barium nitrate was used instea~ of calcium nitrate.
The catalyst 10 thus prepared was subiected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.40 BaO, 0.76 CuO, A12O3 and 23.3 SiO2.
ExamPle 13 The catalysts prepared in Example Nos. 10, 11, and 12 were used for evaluation of the catalytic decomposi-tion performance in the same manner as that of Example ~.
The NO conversions at respective temperatures are shown in Table 4.

Table 4 NO conversion (%) Temp.
Catalyst Catalyst Catalyst ExamPle 14 An aqueous sodium silicate solution (SiO2:
153 g~liter; Na2O: 50 g/liter; A12O3: 0.8 g/liter) and an aqueous aluminum sulfate solution (A12O3:
38.4 g/liter; H2SO4: 275 g/liter) were continuously fed respectively at rates of 3.2 liters/hr and 0.8 liter/hr into an overflow type reactor having a net volume of 2 liters, while stirring. The reaction temperature was 30 to 32C, and the pH of the discharged slurry was 6.4 to 6.6.
The discharged slurry was subjected to solid-liquid separation, and the solid was thoroughly washed with ~water to obtain a granular amorphous aluminosilicate uniform compound having an Na2O content of 1.72% by weight an A12O3 content of 2.58~ by weight, an SiO2 content of 39.3~ by weight, and an H2O content of 56.4%
by weight. An autoclave was charged with 2,840 g of the uniform compound and 5,160 g of a 1.39% by weight aqueous NaOH solution, and crystallization was effected at 160C for 72 hr with stirring. The product was subjected to solid-liquid separation, and the solid was washed with water and dried to obtain a ZSM-5 type zeolite. The zeolite was subjected to chemical ~0 analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
1.1 Na2O, A12O3 and 23.3 SiO2.
To one liter of a 0.012 N aqueous yttrium nitrate solution was added 10 g of this zeolite. The mixture was stirred at 60C for one day and then washed to obtain a zeolite ion-exchanged with yttrium. Subse-quently, the zeolite thus obtained was added to one liter of a 0.024 N aqueous copper acetate solution. The mixture was stirred at 60C for one day, washed and dried to prepare a catalyst 11. The catalyst 11 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.28 Y2O3 , 1.05 CuO, A12O3 and 23.3 SiO2.
Exam~le 15 The catalyst prepared in Example 14 was used for an evaluation of the catalytic decomposition performance, in the same manner as that of Example 5.
The conversions of NO into N2 at respective temperatures are given in Table 5.

Table 5 Temp.Conversion t%) into N2 ComParative Example 3 To one liter of a 0.024 N aqueous copper acetate solution was added 10 g of the ZSM-5 type zeolite prepared in Example 15. The mixture was stirred at 60C
for one day, washed and dried to prepare a comparative catalyst 2. The comparative catalyst 2 thus prepared was su~ected to chemical analysis, and as a result, found to have the following composition in terms of mole 0 ratios on an anhydrous basis:
0.15 Na2O, 1.33 CuO, Al2O3 and 23.3 SiO2.
ComParative Example 4 To one liter of a 0.012 N aqueous yttrium nitrate solution was added 10 g of the ZSM-5 type zeolite prepared in Example 15. The mixture was stirred at 60C
for one day, washed and dried to prepare a comparative catalyst 3. The comparative catalyst 3 thus prepared was su~jected to chemical analysis, and as a result, found to have the following composition in terms of mole 0 ratios on an anhydrous basis:
0-75 Y2O3 , Al2O3 and 23.3 SiO2.
Comparative ExamPle 5 The catalyst prepared in Comparative Examples 3 and 4 was used for evaluation of the catalytic decompo-sition performance in the same manner as that ofExample 5.
The results are shown in Ta~le 6.

- 17 - 20'~781~

Table 6 Temp. Conversion (~) into N2 Comparative catalyst -ExamPle 16 An aqueous sodium silicate solution (SiO2: 153 g/liter; Na2O: 50 g/liter; A12O3: 0.8 g/liter) and an aqueous aluminum sulfate solution (A12O3: 38.4 g~liter;
SO4: 275 g/liter) were continuously fed respectively at rates of 3.2 liters/hr and 0.8 liter/hr into an overflow type reactor having a net volume of 2 liters, while stirring. The reaction temperature was 30 to 32C, and the pH of the discharged slurry was 6.4 to 6.6.
The discharged slurry was subjected to slid-liquid separation, and the solid was thoroughly washed with water to obtain a granular amorphous aluminosilichte uniform compound having an Na2O content of 1.72~ by weight, an A12O3 content of 2.58~ by weight, an SiO2 content of 39.3% by weight, and an H2O content of 56.4%
by weight. An autoclave was charged with 2,840 g of the uniform compound and 5,160 g of a 1.39~ by weight aqueous NaOH solution, and crystallization was effected at 160C for 72 hr with stirring. The product was subjected to solid-liquid separation, and the solid was washed with water and dried to obtain a ZSM-5 type zeolite. The zeolite was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios o~ oxides on an - 18 - 20~78~

anhydrous basis:
1-1 Na2' Al23 and 23-3 Si2 To one liter of a 0.012 N aqueous silver nitrate solution was added 10 g of this zeolite. The mixture was stirred at bOC for one day under a light-shielded condition and then washed to obtain a zeolite ion-exchanged with silver. Subsequently, the zeolite thus obtained was added to one liter of a 0.024 N aqueous copper acetate solution. The mixture was stirred at 60C for one day under a light-shielded condition, washed and dried to prepare a catalyst 12. The catalyst 12 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.32 Ag20, 1.01 CuO, Al203 and 23.3 SiO2.
Example 17 The catalyst prepared in Example 16 was used for an evaluation of the catalytic decomposition performance, in the same manner as that of Example 5.
The conversions of NO into N2 at respective temperatures are given in Table 7.

Table 7 Temp. Conversion (%) into N2 ComParative Example 6 To one liter of a 0.012 N aqueous silver nitrate solution was added 10 g of the ZSM-5 type zeolite prepared in Example 16. The mixture was stirred at 60C
for one day under a light-shielded condition, washed, lg- 2~3781~
and dried to prepare a comparative catalyst 4. The comparative catalyst 4 thus prepared was subjected to chemical analysis, and as a result, found to have the following composition in terms of mole ratios of oxides on an anhydrous basis:
0.95 Ag2O, A12O3 and 23.3 SiO2.
ComParative Example 7 The catalyst prepared in Comparative Example 6 was used for an evaluation of the catalytic decomposition performance, in the same manner as that of Example 5.
The results are given in Table 8.

Table 8 Temp.Conversion (%) into N2 Comparative Catalyst 550C o 600C o

Claims

1. A catalyst for catalytically decomposing nitrogen oxides, comprising a zeolite having a mole ratio of SiO2/Al2O3 of at least 20 and containing copper ions and transition metal ions other than copper ions.

2. A catalyst for catalytically decomposing nitrogen oxides, comprising a zeolite having a mole ratio of SiO2/Al2O3 of at least 20 and containing copper ions and at least one alkaline earth metal ions selected from the group consisting of calcium, strontium and barium ions.

3. A catalyst for catalytically decomposing nitrogen oxides, comprising a zeolite having a mole ratio of SiO2/Al2O3 of at least 20, and containing copper ions and yttrium ions.

4. A catalyst for catalytically decomposing nitrogen oxides, comprising a zeolite having a mole ratio of SiO2/Al2O3 of at least 20, and containing copper ions and silver ions.

5. A method of removing nitrogen oxides from a gas containing the same by catalytically decomposing the nitrogen oxide, which comprises bringing a catalyst into contact with the gas containing nitrogen oxides, said catalyst comprising a zeolite having a mole ratio of SiO2/Al2O3 of at least 20 and containing (i) copper ions and (ii) (a) transition metal ions other than copper ions, (b) at least one alkaline earth metal ion selected from calcium, strontium, and barium ions, (c) yttrium ions, or (d) silver ions.